Biological Sciences Division, Pacific Northwest National Laboratory, 3300 Stevens Dr., Richland, WA 99354, USA.
Department of Environmental Health and Engineering, Johns Hopkins University, 3400 North Charles Street, Baltimore, MD 21218-2686, USA; Department of Civil and Environmental Engineering, The University of Texas at San Antonio, 1 UTSA Cir San Antonio, TX 78249, USA.
Sci Total Environ. 2019 Feb 25;653:1377-1394. doi: 10.1016/j.scitotenv.2018.11.026. Epub 2018 Nov 6.
The feasibility of generating a lipid-containing algal-bacterial polyculture biomass in municipal primary wastewater and enhancing biomethanation of lipid-extracted algal residues (LEA) through hydrothermal pretreatment and co-digestion with sewage sludge (SS) was investigated. In high-rate algal ponds, the polyculture of native algal and bacteria species demonstrated a monthly average net and gross biomass productivity of 30 ± 3 and 36 ± 3 g m day (summer season). The algal community was dominated by Micractinium sp. followed by Scenedesmus sp., Chlorella sp., pennate diatoms and Chlamydomonas sp. The polyculture metabolic activities resulted in average reductions of wastewater volatile suspended solids (VSS), carbonaceous soluble biochemical oxygen demand (csBOD) and total nitrogen (N) of 63 ± 18%, 98 ± 1% and 76 ± 21%, respectively. Harvested biomass contained nearly 23% lipid content and an extracted blend of fatty acid methyl esters satisfied the ASTM D6751 standard for biodiesel. Anaerobic digestion of lipid extracted algal residues (LEA) demonstrated long lag-phase in methane production of 17 days and ultimate methane yield of 296 ± 2 mL/gVS (or ~50% of theoretical), likely because to its limited biodegradability and toxicity due to presence of the residual solvent (hexane). Hydrothermal pretreatment increased the ultimate methane yield and production rate by 15-30% but did not mitigate solvent toxicity effects completely leading to less substantial improvement in energy output of 5-20% and diminished Net Energy Ratio (NER < 1). In contrast, co-digestion of LEA with sewage sludge (10% to 90% ratio) was found to minimize solvent toxicity and improve methane yield enhancing the energy output ~4-fold, compared to using LEA as a single substrate, and advancing NER to 4.2.
研究了在城市一级污水中生成含脂藻类-细菌共培养生物量的可行性,并通过水热处理预处理和与污水污泥 (SS) 共消化来增强提取脂类后的藻类残余物 (LEA) 的生物甲烷化。在高负荷藻类池塘中,本地藻类和细菌物种的共培养表现出每月平均净生物量和总生物量生产力分别为 30 ± 3 和 36 ± 3 g m-2 day-1(夏季)。藻类群落以 Micractinium sp.为主,其次是 Scenedesmus sp.、Chlorella sp.、羽纹硅藻和 Chlamydomonas sp.。共培养的代谢活性导致废水挥发性悬浮固体 (VSS)、碳源可生化需氧量 (csBOD) 和总氮 (N) 分别平均减少 63 ± 18%、98 ± 1%和 76 ± 21%。收获的生物质含有近 23%的脂质含量,提取的脂肪酸甲酯混合物符合 ASTM D6751 生物柴油标准。提取脂类后的藻类残余物 (LEA) 的厌氧消化在甲烷生成方面表现出 17 天的长迟滞期和最终甲烷产量为 296 ± 2 mL/gVS(或约 50%的理论值),这可能是由于其有限的生物降解性和由于存在残留溶剂(己烷)而产生的毒性。水热处理预处理将最终甲烷产量和产率提高了 15-30%,但并未完全减轻溶剂毒性的影响,导致能源输出的实质性改善仅为 5-20%,净能量比 (NER < 1) 降低。相比之下,与污水污泥(10%到 90%的比例)共消化发现可以最小化溶剂毒性并提高甲烷产量,与单独使用 LEA 相比,能源输出提高了约 4 倍,并且净能量比提高到 4.2。